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Factors affecting the rates of arsine evolution and arsenical mineralization in soil.

机译:影响土壤中砷演化和砷矿化速率的因素。

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Effects of soil moisture, temperature, arsenic compounds, concentration of As, and cellulose addition on arsine evolution and demethylation of organic arsenicals were studied in Sacramento silty clay amended with As and incubated for 70 days. Volatile arsines were not detected over a gamma radiation sterilized soil, suggesting that arsine evolution in soil is a microbial process. When 100 mg As kg{dollar}sp{lcub}-1{rcub}{dollar} soil as sodium cacodylate was incorporated into the soil, the maximum arsine evolution occurred at a soil moisture level of 350 mg H{dollar}sb2{dollar}O kg{dollar}sp{lcub}-1{rcub}{dollar} (around {dollar}-1/3{dollar} bar) between 0-50 days and at a level of 250 mg H{dollar}sb2{dollar}O kg{dollar}sp{lcub}-1{rcub}{dollar} soil after 50 days. Total arsine production was higher at 25{dollar}spcirc{dollar}C than at 5{dollar}spcirc{dollar}C. At 5{dollar}spcirc{dollar}C, a relatively low and constant arsine evolution rate occurred, suggesting zero order kinetics. Biodegradation kinetics models were fit the data at 25{dollar}spcirc{dollar}C. The Monod model with growth and the two-compartment model gave the best fit. Total arsine production from soil amended with at rates of 100 mg As kg{dollar}sp{lcub}-1{rcub}{dollar} soil followed the order: sodium cacodylate (CA) {dollar}>{dollar} monomethylarsonic acid (MMAA) {dollar}>{dollar} sodium arsenite {dollar}>{dollar} sodium arsenate. Arsine evolution increased linearly with soil cacodylate concentration in the range of 0-100 mg As kg{dollar}sp{lcub}-1{rcub}{dollar} soil (R{dollar}sp2{dollar} = 0.99). Cellulose addition (0-5%, w/w) enhanced arsine production linearly (R{dollar}sp2{dollar} = 0.99).; Demethylation of CA increased as soil moisture increased from 50 to 550 mg H{dollar}sb2{dollar}O kg{dollar}sp{lcub}-1{rcub}{dollar} soil. More CA was demethylated at 25{dollar}spcirc{dollar}C than at 5{dollar}spcirc{dollar}C. The percentage of CA demethylated decreased as its initial concentration increased. Cellulose addition depressed CA demethylation indicating preferential microbial utilization of cellulose over CA. The rate of MMAA demethylation was lower than that for CA under the same conditions. The overall percentage of CA and MMAA demethylated after 70 days was much higher (3-87%) than arsine evolution (0.001-0.4%).; An experimental data based model was developed to predict the fate of soil arsenicals. Arsenic transformations were assumed to follow first order kinetics. The rate coefficients were calculated based on the arsenic species concentration measured after 70 days of incubation. The model predicts that degradation of CA over two years results in 99.8% conversion to arsenate and {dollar}<{dollar}0.2% evolution as arsines. Arsenic will accumulate in the soil from arsenical usage.
机译:研究了土壤水分,温度,砷化合物,砷的浓度和纤维素的添加对砷在有机硅改性的萨克拉曼多粉质粘土中保温和保温70天的影响,从而对砷的释放和有机砷的去甲基化产生了影响。在经过伽马射线灭菌的土壤中未检测到挥发性的砷化氢,表明土壤中的砷化氢进化是微生物过程。当将100 mg As kg {dollar} sp {lcub} -1 {rcub} {dollar}土壤作为草甘膦掺入土壤中时,在土壤湿度为350 mg H {dollar} sb2 {dollar } 0至50天之间的250千克H {dollar} sb2 {}} {kg} {dol}} {lcub} -1 {rcub} {dol}(约{dol} -1/3 {dol} bar){ 50天后,每公斤土壤{kg} sp {lcub} -1 {rcub} {dollar}美元。 a的总产量在25℃时比在5℃时高。在5spspcirc {dollar} C,发生了相对较低且恒定的a演化速率,表明动力学为零级。生物降解动力学模型适合于25 {spcirc {dollar} C的数据。具有增长的Monod模型和两室模型最适合。以100 mg As kg {dollar} sp {lcub} -1 {rcub} {dollar}土壤改良的砷总产量按以下顺序排列:ca酸钠(CA){dollar}> {dollar}一甲基ar磺酸(MMAA ){美元}> {美元}亚砷酸钠{美元}> {美元}砷酸钠。砷的演变随着土壤草酸盐浓度在0-100 mg As kg {dol} sp {lcub} -1 {rcub} {dol}土壤中的线性增加(R {dollar} sp2 {dollar} = 0.99)。纤维素的添加(0-5%,w / w)线性地提高了ine的产生(R {dollar} sp2 {dollar} = 0.99)。随着土壤水分从50 mg / kg升高到550 mg H {dollar} sb2 {dollar} Okg {dollar} sp {lcub} -1 {rcub} {dollar}土壤,CA的脱甲基作用增加。在25℃时,更多的CA去甲基化,而在5℃时则更多。 CA脱甲基的百分比随其初始浓度的增加而降低。纤维素的添加抑制了CA的去甲基化,表明纤维素的微生物利用率高于CA。在相同条件下,MMAA脱甲基率低于CA。 70天后脱甲基化的CA和MMAA的总百分比(3-87%)比砷化氢(0.001-0.4%)高得多。建立了基于实验数据的模型来预测土壤砷的命运。假定砷的转化遵循一级动力学。速率系数是根据孵育70天后测得的砷物种浓度计算得出的。该模型预测,两年多来CA的降解将导致99.8%的砷化物转化为砷酸盐,{的转化率为{dollar} <{dollar} 0.2%。砷会因砷的使用而积聚在土壤中。

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